JPH02177821A - Bacterial biomass fertilizer - Google Patents
Bacterial biomass fertilizerInfo
- Publication number
- JPH02177821A JPH02177821A JP1279614A JP27961489A JPH02177821A JP H02177821 A JPH02177821 A JP H02177821A JP 1279614 A JP1279614 A JP 1279614A JP 27961489 A JP27961489 A JP 27961489A JP H02177821 A JPH02177821 A JP H02177821A
- Authority
- JP
- Japan
- Prior art keywords
- weight
- fertilizer
- bacterial biomass
- fermentation
- liquid phase
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- 239000002028 Biomass Substances 0.000 title claims abstract description 58
- 239000003337 fertilizer Substances 0.000 title claims abstract description 53
- 230000001580 bacterial effect Effects 0.000 title claims description 58
- 238000000855 fermentation Methods 0.000 claims abstract description 41
- 230000004151 fermentation Effects 0.000 claims abstract description 41
- WSFSSNUMVMOOMR-UHFFFAOYSA-N Formaldehyde Chemical compound O=C WSFSSNUMVMOOMR-UHFFFAOYSA-N 0.000 claims abstract description 21
- 239000007791 liquid phase Substances 0.000 claims abstract description 18
- 239000003242 anti bacterial agent Substances 0.000 claims abstract description 7
- 229940088710 antibiotic agent Drugs 0.000 claims abstract description 6
- 235000001674 Agaricus brunnescens Nutrition 0.000 claims abstract 3
- 238000004519 manufacturing process Methods 0.000 claims description 24
- 238000009264 composting Methods 0.000 claims description 15
- 238000000034 method Methods 0.000 claims description 15
- 235000015097 nutrients Nutrition 0.000 claims description 15
- 229930182555 Penicillin Natural products 0.000 claims description 13
- JGSARLDLIJGVTE-MBNYWOFBSA-N Penicillin G Chemical compound N([C@H]1[C@H]2SC([C@@H](N2C1=O)C(O)=O)(C)C)C(=O)CC1=CC=CC=C1 JGSARLDLIJGVTE-MBNYWOFBSA-N 0.000 claims description 13
- 229940049954 penicillin Drugs 0.000 claims description 13
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 12
- 230000003115 biocidal effect Effects 0.000 claims description 12
- 239000000203 mixture Substances 0.000 claims description 12
- 239000010815 organic waste Substances 0.000 claims description 8
- 238000011081 inoculation Methods 0.000 claims description 7
- SWHAQEYMVUEVNF-UHFFFAOYSA-N magnesium potassium Chemical compound [Mg].[K] SWHAQEYMVUEVNF-UHFFFAOYSA-N 0.000 claims description 6
- 229910052757 nitrogen Inorganic materials 0.000 claims description 6
- 229910001385 heavy metal Inorganic materials 0.000 claims description 4
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 3
- 239000005416 organic matter Substances 0.000 claims description 3
- 239000001301 oxygen Substances 0.000 claims description 3
- 229910052760 oxygen Inorganic materials 0.000 claims description 3
- 239000003795 chemical substances by application Substances 0.000 claims description 2
- 230000003472 neutralizing effect Effects 0.000 claims description 2
- CPLXHLVBOLITMK-UHFFFAOYSA-N Magnesium oxide Chemical compound [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 claims 6
- 239000000395 magnesium oxide Substances 0.000 claims 3
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 claims 1
- 229910052700 potassium Inorganic materials 0.000 claims 1
- 239000011591 potassium Substances 0.000 claims 1
- 239000002361 compost Substances 0.000 abstract description 23
- 241000894006 Bacteria Species 0.000 abstract description 6
- 239000000463 material Substances 0.000 abstract description 4
- 238000000354 decomposition reaction Methods 0.000 abstract description 3
- 230000000050 nutritive effect Effects 0.000 abstract 3
- 239000007788 liquid Substances 0.000 description 14
- 239000000047 product Substances 0.000 description 11
- 238000003306 harvesting Methods 0.000 description 9
- 235000008331 Pinus X rigitaeda Nutrition 0.000 description 8
- 235000011613 Pinus brutia Nutrition 0.000 description 8
- 241000018646 Pinus brutia Species 0.000 description 8
- 241000121220 Tricholoma matsutake Species 0.000 description 6
- 239000002002 slurry Substances 0.000 description 6
- 239000002699 waste material Substances 0.000 description 6
- 239000002351 wastewater Substances 0.000 description 6
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 6
- 239000010902 straw Substances 0.000 description 5
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 4
- 235000011941 Tilia x europaea Nutrition 0.000 description 4
- 239000004571 lime Substances 0.000 description 4
- 239000000654 additive Substances 0.000 description 3
- 239000003674 animal food additive Substances 0.000 description 3
- 238000000926 separation method Methods 0.000 description 3
- 239000007787 solid Substances 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 229920001817 Agar Polymers 0.000 description 2
- 241000233866 Fungi Species 0.000 description 2
- 108091005804 Peptidases Proteins 0.000 description 2
- 244000046052 Phaseolus vulgaris Species 0.000 description 2
- 235000010627 Phaseolus vulgaris Nutrition 0.000 description 2
- 239000004365 Protease Substances 0.000 description 2
- AUNGANRZJHBGPY-SCRDCRAPSA-N Riboflavin Chemical compound OC[C@@H](O)[C@@H](O)[C@@H](O)CN1C=2C=C(C)C(C)=CC=2N=C2C1=NC(=O)NC2=O AUNGANRZJHBGPY-SCRDCRAPSA-N 0.000 description 2
- 235000019764 Soybean Meal Nutrition 0.000 description 2
- 244000299461 Theobroma cacao Species 0.000 description 2
- 235000009470 Theobroma cacao Nutrition 0.000 description 2
- 230000000996 additive effect Effects 0.000 description 2
- 241001148470 aerobic bacillus Species 0.000 description 2
- 239000008272 agar Substances 0.000 description 2
- 238000007796 conventional method Methods 0.000 description 2
- 238000001035 drying Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000011010 flushing procedure Methods 0.000 description 2
- 230000002538 fungal effect Effects 0.000 description 2
- JVTAAEKCZFNVCJ-UHFFFAOYSA-N lactic acid Chemical compound CC(O)C(O)=O JVTAAEKCZFNVCJ-UHFFFAOYSA-N 0.000 description 2
- 238000009928 pasteurization Methods 0.000 description 2
- 239000002689 soil Substances 0.000 description 2
- 239000004455 soybean meal Substances 0.000 description 2
- 239000000758 substrate Substances 0.000 description 2
- 239000000725 suspension Substances 0.000 description 2
- 241000222518 Agaricus Species 0.000 description 1
- 235000019737 Animal fat Nutrition 0.000 description 1
- DKPFZGUDAPQIHT-UHFFFAOYSA-N Butyl acetate Natural products CCCCOC(C)=O DKPFZGUDAPQIHT-UHFFFAOYSA-N 0.000 description 1
- 229930186147 Cephalosporin Natural products 0.000 description 1
- -1 Copper Zinc Manganese Iron Lead Cadmium Chromium Cobalt Nickel Chemical compound 0.000 description 1
- PMATZTZNYRCHOR-CGLBZJNRSA-N Cyclosporin A Chemical compound CC[C@@H]1NC(=O)[C@H]([C@H](O)[C@H](C)C\C=C\C)N(C)C(=O)[C@H](C(C)C)N(C)C(=O)[C@H](CC(C)C)N(C)C(=O)[C@H](CC(C)C)N(C)C(=O)[C@@H](C)NC(=O)[C@H](C)NC(=O)[C@H](CC(C)C)N(C)C(=O)[C@H](C(C)C)NC(=O)[C@H](CC(C)C)N(C)C(=O)CN(C)C1=O PMATZTZNYRCHOR-CGLBZJNRSA-N 0.000 description 1
- 108010036949 Cyclosporine Proteins 0.000 description 1
- AUNGANRZJHBGPY-UHFFFAOYSA-N D-Lyxoflavin Natural products OCC(O)C(O)C(O)CN1C=2C=C(C)C(C)=CC=2N=C2C1=NC(=O)NC2=O AUNGANRZJHBGPY-UHFFFAOYSA-N 0.000 description 1
- 244000068988 Glycine max Species 0.000 description 1
- 235000010469 Glycine max Nutrition 0.000 description 1
- 241000186660 Lactobacillus Species 0.000 description 1
- 102000035195 Peptidases Human genes 0.000 description 1
- 235000007685 Pleurotus columbinus Nutrition 0.000 description 1
- 240000001462 Pleurotus ostreatus Species 0.000 description 1
- 235000001603 Pleurotus ostreatus Nutrition 0.000 description 1
- 102100037486 Reverse transcriptase/ribonuclease H Human genes 0.000 description 1
- 235000021355 Stearic acid Nutrition 0.000 description 1
- 229930003779 Vitamin B12 Natural products 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 239000013543 active substance Substances 0.000 description 1
- 238000007792 addition Methods 0.000 description 1
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 description 1
- 229910052921 ammonium sulfate Inorganic materials 0.000 description 1
- 235000011130 ammonium sulphate Nutrition 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000001913 cellulose Substances 0.000 description 1
- 229920002678 cellulose Polymers 0.000 description 1
- 238000005119 centrifugation Methods 0.000 description 1
- 229940124587 cephalosporin Drugs 0.000 description 1
- 150000001780 cephalosporins Chemical class 0.000 description 1
- 229960005091 chloramphenicol Drugs 0.000 description 1
- WIIZWVCIJKGZOK-RKDXNWHRSA-N chloramphenicol Chemical compound ClC(Cl)C(=O)N[C@H](CO)[C@H](O)C1=CC=C([N+]([O-])=O)C=C1 WIIZWVCIJKGZOK-RKDXNWHRSA-N 0.000 description 1
- 229960001265 ciclosporin Drugs 0.000 description 1
- AGVAZMGAQJOSFJ-WZHZPDAFSA-M cobalt(2+);[(2r,3s,4r,5s)-5-(5,6-dimethylbenzimidazol-1-yl)-4-hydroxy-2-(hydroxymethyl)oxolan-3-yl] [(2r)-1-[3-[(1r,2r,3r,4z,7s,9z,12s,13s,14z,17s,18s,19r)-2,13,18-tris(2-amino-2-oxoethyl)-7,12,17-tris(3-amino-3-oxopropyl)-3,5,8,8,13,15,18,19-octamethyl-2 Chemical compound [Co+2].N#[C-].[N-]([C@@H]1[C@H](CC(N)=O)[C@@]2(C)CCC(=O)NC[C@@H](C)OP(O)(=O)O[C@H]3[C@H]([C@H](O[C@@H]3CO)N3C4=CC(C)=C(C)C=C4N=C3)O)\C2=C(C)/C([C@H](C\2(C)C)CCC(N)=O)=N/C/2=C\C([C@H]([C@@]/2(CC(N)=O)C)CCC(N)=O)=N\C\2=C(C)/C2=N[C@]1(C)[C@@](C)(CC(N)=O)[C@@H]2CCC(N)=O AGVAZMGAQJOSFJ-WZHZPDAFSA-M 0.000 description 1
- 229930182912 cyclosporin Natural products 0.000 description 1
- 238000010908 decantation Methods 0.000 description 1
- 235000014113 dietary fatty acids Nutrition 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 239000000194 fatty acid Substances 0.000 description 1
- 229930195729 fatty acid Natural products 0.000 description 1
- 150000004665 fatty acids Chemical class 0.000 description 1
- 239000002921 fermentation waste Substances 0.000 description 1
- 238000009472 formulation Methods 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 239000003979 granulating agent Substances 0.000 description 1
- 239000010440 gypsum Substances 0.000 description 1
- 229910052602 gypsum Inorganic materials 0.000 description 1
- 231100001261 hazardous Toxicity 0.000 description 1
- 239000000383 hazardous chemical Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- FUZZWVXGSFPDMH-UHFFFAOYSA-N hexanoic acid Chemical compound CCCCCC(O)=O FUZZWVXGSFPDMH-UHFFFAOYSA-N 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 239000004310 lactic acid Substances 0.000 description 1
- 235000014655 lactic acid Nutrition 0.000 description 1
- WSFSSNUMVMOOMR-NJFSPNSNSA-N methanone Chemical compound O=[14CH2] WSFSSNUMVMOOMR-NJFSPNSNSA-N 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 235000010755 mineral Nutrition 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 239000010841 municipal wastewater Substances 0.000 description 1
- 239000010955 niobium Substances 0.000 description 1
- GUCVJGMIXFAOAE-UHFFFAOYSA-N niobium atom Chemical compound [Nb] GUCVJGMIXFAOAE-UHFFFAOYSA-N 0.000 description 1
- 235000021049 nutrient content Nutrition 0.000 description 1
- QIQXTHQIDYTFRH-UHFFFAOYSA-N octadecanoic acid Chemical compound CCCCCCCCCCCCCCCCCC(O)=O QIQXTHQIDYTFRH-UHFFFAOYSA-N 0.000 description 1
- OQCDKBAXFALNLD-UHFFFAOYSA-N octadecanoic acid Natural products CCCCCCCC(C)CCCCCCCCC(O)=O OQCDKBAXFALNLD-UHFFFAOYSA-N 0.000 description 1
- 239000003960 organic solvent Substances 0.000 description 1
- 238000005504 petroleum refining Methods 0.000 description 1
- 230000000243 photosynthetic effect Effects 0.000 description 1
- 239000010908 plant waste Substances 0.000 description 1
- 244000144977 poultry Species 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 229960002477 riboflavin Drugs 0.000 description 1
- 235000019192 riboflavin Nutrition 0.000 description 1
- 239000002151 riboflavin Substances 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 230000002000 scavenging effect Effects 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 238000002791 soaking Methods 0.000 description 1
- 159000000000 sodium salts Chemical class 0.000 description 1
- 238000001694 spray drying Methods 0.000 description 1
- 238000005507 spraying Methods 0.000 description 1
- 239000007858 starting material Substances 0.000 description 1
- 239000008117 stearic acid Substances 0.000 description 1
- 230000001954 sterilising effect Effects 0.000 description 1
- 238000004659 sterilization and disinfection Methods 0.000 description 1
- 235000000346 sugar Nutrition 0.000 description 1
- 150000008163 sugars Chemical class 0.000 description 1
- 239000013589 supplement Substances 0.000 description 1
- 230000001502 supplementing effect Effects 0.000 description 1
- 239000008399 tap water Substances 0.000 description 1
- 235000020679 tap water Nutrition 0.000 description 1
- 239000011573 trace mineral Substances 0.000 description 1
- 235000013619 trace mineral Nutrition 0.000 description 1
- 235000013343 vitamin Nutrition 0.000 description 1
- 239000011782 vitamin Substances 0.000 description 1
- 229930003231 vitamin Natural products 0.000 description 1
- 229940088594 vitamin Drugs 0.000 description 1
- 239000011715 vitamin B12 Substances 0.000 description 1
- 235000019163 vitamin B12 Nutrition 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
- 239000002023 wood Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F11/00—Other organic fertilisers
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G18/00—Cultivation of mushrooms
- A01G18/20—Culture media, e.g. compost
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F5/00—Fertilisers from distillery wastes, molasses, vinasses, sugar plant or similar wastes or residues, e.g. from waste originating from industrial processing of raw material of agricultural origin or derived products thereof
- C05F5/006—Waste from chemical processing of material, e.g. diestillation, roasting, cooking
- C05F5/008—Waste from biochemical processing of material, e.g. fermentation, breweries
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Mycology (AREA)
- Environmental Sciences (AREA)
- Engineering & Computer Science (AREA)
- Biotechnology (AREA)
- Botany (AREA)
- Environmental & Geological Engineering (AREA)
- Fertilizers (AREA)
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
- Mushroom Cultivation (AREA)
Abstract
Description
【発明の詳細な説明】
(産業上のキ1]用分野)
この発明は、細菌バイオマス、その製法およびマツシュ
ルーム製造における捕捉栄養物としての有機肥料の用途
に関する。かかる肥料は、特に、工程の窒素源として使
用しうる。この方法では、菌糸体は、水中に懸濁され、
その後、該懸濁液を鉱酸でpH5以下にし、次いで、水
性菌糸体懸濁液を150〜300℃でのスプレィ乾燥に
付している。EP60407号は、ペニシリン非含有・
菌子体塊をペニシリン生産用培地(+!ii潤菌糸体)
から製造する方法を記載しているが、ここでは、残った
ペニシリンは、湿潤菌糸体をペニシリン耐性乳酸桿菌の
使用により嫌気性乳酸発酵に付するような方法で、除去
している。さらに、GB649818号は、ペニシリン
発酵の廃棄物を用いうる旨記載しており、ここでは、固
体発酵残渣を栄養物に添加して、例えばビタミンB12
やリボフラビンを製造している。また、ペニシリン発酵
から得られる飼料添加物の製造も知られており、083
92864号はペニシリン製造からの菌糸体廃棄物を、
飼料添加物として使用すべく加圧下1こ140〜200
℃に加熱し、次いで乾燥することからなる方法を開示し
ている。DETAILED DESCRIPTION OF THE INVENTION Field of the Invention This invention relates to bacterial biomass, its production and the use of organic fertilizers as scavenging nutrients in pine mushroom production. Such fertilizers can be used, inter alia, as a nitrogen source in the process. In this method, mycelium is suspended in water;
Thereafter, the suspension is brought to a pH below 5 with mineral acid, and the aqueous mycelium suspension is then subjected to spray drying at 150-300°C. EP60407 does not contain penicillin.
The mycelium mass is used as a medium for penicillin production (+!ii wet mycelium)
In this case, residual penicillin is removed by subjecting the wet mycelium to anaerobic lactic acid fermentation using penicillin-resistant lactobacilli. Furthermore, GB 649818 states that waste products of penicillin fermentation can be used, where solid fermentation residues are added to nutrients to obtain vitamin B12, for example.
and riboflavin. Also known is the production of feed additives obtained from penicillin fermentation, 083
No. 92864 uses mycelium waste from penicillin production,
1 piece under pressure for use as a feed additive 140-200
A method is disclosed consisting of heating to 0.degree. C. and then drying.
世界中において、種々の供給源の廃水やスラリコンポス
ト(compost)工程の改善に、また真菌類菌糸体
の直接栄養源として適している。この発明の細菌バイオ
マスは、抗生物質の発酵工程で得られる液体有機廃棄物
から得られる。液体有機廃棄物(以下、液相と呼ぶ。)
は、抗生物質が単離、除去される抗生物質発酵の液体成
分を意味する。この発明の細菌バイオマスは、いイつゆ
る液相を倒加的な発酵に付すことにより製造される。所
望により、種々の発酵工程から得られる液体有機廃棄物
を、付加的な発酵前に該液相と合することができる。It is suitable for improving wastewater and slurry composting processes of various sources throughout the world and as a direct nutrient source for fungal mycelium. The bacterial biomass of this invention is obtained from liquid organic waste obtained from antibiotic fermentation processes. Liquid organic waste (hereinafter referred to as liquid phase)
means the liquid component of an antibiotic fermentation from which antibiotics are isolated and removed. The bacterial biomass of this invention is produced by subjecting a so-called liquid phase to additive fermentation. If desired, liquid organic wastes obtained from the various fermentation steps can be combined with the liquid phase before additional fermentation.
(従来の技術)
ペニシリン発酵の廃棄物を用いて種々の生成物を製造す
ることは、文献に記載されている。BE505453号
は肥料の製法を開示しているが、ここでは、セルロース
に対し強力な発酵活性を示すペニシリン発酵の廃棄物を
、コンポストの製造に用いている。DD139083号
は、ペニシリン非含有・乾燥菌糸体生成物の製法を開示
しているが、この生成物は飼料添加物、肥料または発酵
−や肥料製造用の組成物が実際的に使用されている。し
かしながら、廃水の使用については、かかる廃水から除
去した有害物質が通常いわゆるスラリー中に濃縮される
という、1つの問題がある。BACKGROUND OF THE INVENTION The use of penicillin fermentation waste to produce various products has been described in the literature. BE505453 discloses a method for the production of fertilizer, in which the waste of penicillin fermentation, which exhibits a strong fermentation activity towards cellulose, is used for the production of compost. DD 139083 discloses a method for producing a penicillin-free dry mycelium product which is practically used as a feed additive, fertilizer or composition for fermentation and fertilizer production. However, one problem with the use of wastewater is that the harmful substances removed from such wastewater are usually concentrated in a so-called slurry.
この問題処理のための1つの方法は、DE261796
4号に記載されており、ここでは、スラリーを力焼石灰
と混合しているが、この混合物は、完全な肥料として使
用することができる。One way to handle this problem is DE261796
No. 4, in which the slurry is mixed with calcined lime, and this mixture can be used as a complete fertilizer.
細菌を封入して廃水生成物を分解させることも知られて
いる。特開昭36−40886号は、植物廃棄物、未処
理汚物ケーキおよびおが屑を好気性細菌で発酵させるこ
とからなる有機肥料の製法を開示する。It is also known to encapsulate bacteria to degrade wastewater products. JP-A-36-40886 discloses a method for producing organic fertilizers consisting of fermenting plant waste, untreated sewage cake and sawdust with aerobic bacteria.
生化学的および石油精製からの廃水を用いることは、特
開昭45−14091号に記載されている。ここでは、
肥料に用いられる光合成細菌を種々の有機塩、低級脂肪
酸のナトリウム塩および上記産業の廃水を含む溶液中で
培養している。都市廃水処理プラントのスラリーやコン
ポスト廃棄物などの液体有機廃棄物は、代表的には重金
属または他の有害物質で汚染されている。これ点対照的
に、この発明の細菌バイオマスは、付加的な発酵に使用
される物質が滅菌プロセスから得られるので、実質的に
重金属や他の有害物質を含まない。The use of wastewater from biochemical and petroleum refining is described in JP-A-45-14091. here,
Photosynthetic bacteria used in fertilizers are cultured in a solution containing various organic salts, sodium salts of lower fatty acids, and wastewater from the above industries. Liquid organic wastes, such as slurry and compost waste from municipal wastewater treatment plants, are typically contaminated with heavy metals or other hazardous substances. In contrast, the bacterial biomass of the present invention is substantially free of heavy metals and other harmful substances since the materials used for additional fermentation are obtained from a sterilization process.
もっばら、非有害原料(例えば、大豆ミール、種々のタ
イプの糖類、微量元素およびビタミン類)のみを、活性
物質(例えば、抗生物質、プロテアーゼ)の発酵用に用
いる。その結果、(=J加的な発酵から生産された細菌
バイオマスも、望ましくない重金属または他の有害物質
を含まない。この発明の細菌バイオマスの付加的な利点
は、栄養物の含量が高いことである。かかる栄養物含量
は、都市型スラリーおよびコンポスト廃棄物よりも著し
く多い。Preferably, only non-hazardous raw materials (eg soybean meal, various types of sugars, trace elements and vitamins) are used for the fermentation of active substances (eg antibiotics, proteases). As a result, the bacterial biomass produced from additive fermentation is also free of undesirable heavy metals or other harmful substances. An additional advantage of the bacterial biomass of this invention is that it has a high content of nutrients. The nutrient content is significantly higher than that of municipal slurry and compost waste.
(発明の概要)
この発明によれば、この発明の細菌バイオマス肥料が、
マツツクルーム製造における発酵に特に適していること
が判明した。細菌バイオマス肥料か、予備コンボス1〜
化および直接コンポスト化の両段階のコンポストに対し
、添加することができ(発明の詳説)
この発明の細菌バイオマス肥料は、該肥料にポルムアル
デヒドを添加することにより、さらに、その収量につい
て有用な効果が得られる。ホルムアルデヒドは、有効な
量で存在すれば、該肥料中に含まれる栄養物の放出遅延
に役立つ。lu2当たりに使用される細菌バイオマス量
に応じ、種々の濃度のポルムアルデヒドが収量に対し有
効であるが、ホルムアルデヒドは、−船釣には細菌バイ
オマスの約02〜08重量%で存在させる。多量の細菌
バイオマスに対しては、多量のポルムアルデヒドが栄養
物の放出遅延に必要である。(Summary of the invention) According to this invention, the bacterial biomass fertilizer of this invention
It has been found to be particularly suitable for fermentation in pine mushroom production. Bacterial biomass fertilizer or spare combos 1~
(Detailed Description of the Invention) The bacterial biomass fertilizer of this invention can further have a useful effect on the yield by adding polardehyde to the fertilizer. is obtained. Formaldehyde, when present in an effective amount, helps retard the release of nutrients contained in the fertilizer. Depending on the amount of bacterial biomass used per lu2, various concentrations of formaldehyde are effective on yield, but formaldehyde is present at about 0.2-0.8% by weight of the bacterial biomass for boat fishing. For large amounts of bacterial biomass, large amounts of pomaldehyde are required to retard the release of nutrients.
この発明の肥料に使用される細菌バイオマスの好適な方
法は、以下のとおりである。A preferred method of obtaining bacterial biomass for use in the fertilizer of this invention is as follows.
代表的な抗生物質の発酵液は、真菌類などを含む固体成
分と、抗生物質を含む液体成分からなる。A typical antibiotic fermentation liquid consists of a solid component containing fungi and the like, and a liquid component containing the antibiotic.
固体成分は液体成分から、遠心分離のような任意の通常
の分離法で分離することができる。常法、例えば酢酸ブ
ヂルのような有機溶媒での抽出により、抗生物質を液体
成分から、単離、採取して、る。有機物質(例えは、安
定な肥料およびわら)によりコンボス)・を富化させる
べく、近代のマツツクルーム製造では、種々の生成物、
例えば、大豆生成物類、無機窒素源、家きん肥料、カカ
オ豆生成物、石灰、石こうなどを用いる。この発明の細
菌バイオマスは、種々のコンポスト改良剤を用いるか、
または用いずに、コンポストコ−程に対し特に有用であ
ることが判明した。この発明の細菌バイオマスは、コン
ポストの品質と分解時間並びに生産物の品質と収量の両
方を改善することができる。The solid component can be separated from the liquid component by any conventional separation method, such as centrifugation. The antibiotic is isolated and collected from the liquid component by conventional methods, for example extraction with an organic solvent such as butyl acetate. In modern pine mushroom production, various products,
For example, soybean products, inorganic nitrogen sources, poultry fertilizers, cocoa bean products, lime, gypsum, etc. are used. The bacterial biomass of this invention can be prepared using various compost improvers or
It has been found to be particularly useful for composting processes, either with or without. The bacterial biomass of this invention can improve both compost quality and decomposition time as well as product quality and yield.
「液相」を生成することができる。本明細書において用
いられる「液相」なる語は、抗生物質発酵液から実質的
に全ての抗生物質を取り出した液体成分を意味する。該
液相は、水酸化力ルンウム溶液などの適切な中和剤で処
理して、中和させる。所望により、該液相を、当該液体
有機廃棄物および/または異なる発酵過程で得られる該
廃棄物と合することもできる。付加的なかかる液体有機
廃棄物は、付加的な栄養物および細菌として役立つ。A “liquid phase” can be produced. As used herein, the term "liquid phase" refers to the liquid component from which substantially all of the antibiotic has been removed from the antibiotic fermentation broth. The liquid phase is neutralized by treatment with a suitable neutralizing agent, such as a hydroxide solution. If desired, the liquid phase can also be combined with the liquid organic waste and/or the waste obtained from different fermentation processes. Additional such liquid organic waste serves as additional nutrients and bacteria.
その後、該液相を、撹はん発酵容器のような適当な容器
中で、イ」船釣な発酵に付す。発酵過程の間、該液相は
、好ましくは環境温度またはそれ、にりも僅かに高い温
度、例えば25〜35℃に維持する。好ましくは、該温
度は30°Cに一定に維持する。空気導入のような常法
で、酸素を発酵容器に加える。空気は、具体的なる液組
成に応じ、所定の速度で導入することができるが、代表
的には、該速度は、空気5〜l0i3/1時間・発酵容
量1m3、より好ましくは約7z3/1時間・発酵容f
film3である。かかる空気は、酸素源であると共に
、主要な、発酵工程用の細菌源でもある。発酵容器中に
存在する細菌集団は、利用可能な栄養物を消費して、こ
の発明の細菌バイオマスを形成する。The liquid phase is then subjected to manual fermentation in a suitable vessel, such as a stirred fermentation vessel. During the fermentation process, the liquid phase is preferably maintained at or slightly above ambient temperature, for example from 25 to 35<0>C. Preferably, the temperature is kept constant at 30°C. Oxygen is added to the fermentation vessel by conventional methods such as introducing air. Air can be introduced at a predetermined rate depending on the specific liquid composition, but typically the rate is 5-10i3/1 hour of air per cubic meter of fermentation volume, more preferably about 7z3/1 Time/fermentation volume f
It is film3. Such air is both a source of oxygen and a major source of bacteria for the fermentation process. The bacterial population present in the fermentation vessel consumes the available nutrients and forms the bacterial biomass of this invention.
発酵される細菌集団は、周囲の条件に従い、変化させる
ことができ、−船釣には混合培養である。The bacterial population that is fermented can be varied according to the surrounding conditions - for boat fishing it is a mixed culture.
集団には、しばしばンユードモナス・ニス・ビイ(Ps
eudomonas sp、)、バヂルス・ニス・ビイ
(Baa 111us sp、)および/または一般的
に存在する好気性細菌が包含される。Populations often include Neudomonas nis bii (Ps.
eudomonas sp.), Baa 111us sp.) and/or commonly occurring aerobic bacteria.
20〜24時間の保持時間ののち、PeClSO4のよ
うな沈澱剤を、41%溶液約5〜10Q/発酵容1kl
i3の速度で添加することにより、細菌バイオマスの沈
澱を達成する。デカンテーションのような任意の適当な
分離技術より、分離を行う。分離した湿潤細菌バイオマ
スは、代表的には約85%の残留水を含むので、ドライ
ヤーへの付加的な輸送は、ノック・スラリー・ポンプを
用いて行うことができる。ローターディスク・ドライヤ
ー(接により、造粒化剤、例えば約1%の動物脂または
ステアリン酸を添加することができる。After a holding time of 20-24 hours, add a precipitant such as PeClSO4 to about 5-10 Q of a 41% solution/1 kl of fermentation volume.
Achieve precipitation of the bacterial biomass by adding at a rate of i3. Separation is performed by any suitable separation technique such as decantation. Since the separated wet bacterial biomass typically contains about 85% residual water, additional transport to the dryer can be performed using a knock slurry pump. A granulating agent, for example about 1% animal fat or stearic acid, can be added using a rotor disc dryer.
細菌バイオマス肥料の組成
細菌バイオマス肥料は、以下の平均組成(重量%)を有
する。Composition of Bacterial Biomass Fertilizer Bacterial biomass fertilizer has the following average composition (% by weight):
乾燥物質
有機物質
窒素(有機的に結合)
P、05
に、O
aO
gO
銅
亜鉛
マンガン
鉄
鉛
カドミウム
クロム
コバルト
ニッケル
90〜97%例えば950%
少なくとも・55.0%
4.9〜61%例えば5.5%
39〜5%例えば40%
2.9〜3.7%例えば3.3%
7〜9%例えば8%
08〜14%例えば1.1%
1(1−13ppm例えばllppm
30〜40ppm例えば36ppm
72−80ppm例えば80ppm
5B−70ppm例えば64 fipIll< 6 p
pm例えば< 4 ppm
< 2 ppm例えば< t ppm
<L5ppm例えば<12ppm
< 6 ppm例えば< 4 +1PIn< 6 pp
m例えば< 41)11I11この分析により、有用成
分の含量は充分であることが判明した。変形係数が10
%と仮定すると、殆どの有機肥料について、上記生成物
の著しい変触式ドライヤー)のような適切なドライヤー
により、水分含量を約3〜6%に減少させることができ
る。次いで、細菌バイオマスの乾燥生成物を温度的13
0〜150℃で、4〜8時間加熱する。Dry matter Organic matter Nitrogen (organically bound) P,05 to O aO gO Copper Zinc Manganese Iron Lead Cadmium Chromium Cobalt Nickel 90-97% For example 950% At least 55.0% 4.9-61% For example 5. 5% 39-5% e.g. 40% 2.9-3.7% e.g. 3.3% 7-9% e.g. 8% 08-14% e.g. 1.1% 1 (1-13ppm e.g. llppm 30-40ppm e.g. 36ppm 72-80ppm e.g. 80ppm 5B-70ppm e.g. 64 fipIll<6p
pm e.g. < 4 ppm < 2 ppm e.g. < t ppm < L5ppm e.g. < 12 ppm < 6 ppm e.g. < 4 +1PIN< 6 ppm
m eg < 41) 11I11 This analysis showed that the content of useful components was sufficient. Deformation coefficient is 10
%, for most organic fertilizers the moisture content can be reduced to about 3-6% by a suitable dryer, such as a highly modified convertible dryer of the above products. The dried product of bacterial biomass is then subjected to thermal 13
Heat at 0-150°C for 4-8 hours.
細菌バイオマスを、さらにペレタイザーで加工して、粉
砕可能な粒状物を得る。The bacterial biomass is further processed in a pelletizer to obtain grindable granules.
任意の通常の抗生物質発酵工程で得られた該液相を、こ
の発明に使用できるが、ペニシリン発酵工程の該液相が
、好ましい。所望により該液相と混合される、好適な液
体有機廃棄物源は、種々の抗生物質発酵、例えばセファ
ロスポリンおよびクロラムフェニコール発酵、並びにプ
ロテアーゼおよびシクロスポリン発酵である。Although the liquid phase obtained from any conventional antibiotic fermentation process can be used in this invention, the liquid phase from a penicillin fermentation process is preferred. Suitable liquid organic waste sources, optionally mixed with the liquid phase, are various antibiotic fermentations, such as cephalosporin and chloramphenicol fermentations, and protease and cyclosporine fermentations.
栄養物のバランスを達成するには、苦土カリ肥料を該細
菌バイオマスに混合する。この発明の肥料は、約90〜
96%の細菌バイオマスおよび約4〜10%の苦土カリ
肥料を含有し、好ましくは、約94%の細菌バイオマス
および6%の苦土カリ肥料を含有する。好適な苦土カリ
肥料は、例えばパテントカリ(Patentkali、
商標名)である。所望】2
形例を期待することができる。To achieve nutrient balance, magnesium potassium fertilizer is mixed into the bacterial biomass. The fertilizer of this invention is about 90~
Contains 96% bacterial biomass and about 4-10% magnesium potassium fertilizer, preferably about 94% bacterial biomass and 6% magnesium potassium fertilizer. Suitable magnesium potassium fertilizers include, for example, Patentkali,
Trademark name). Desired] 2. Examples can be expected.
(実施例)
つぎに、実施例を挙げてこの発明をさらに詳しく説明す
るが、これらに限定されるものではない。(Example) Next, the present invention will be explained in more detail by giving examples, but the present invention is not limited thereto.
以下の実施例において、この発明の細菌バイオマス肥料
についての用途を説明する。The following examples illustrate the use of bacterial biomass fertilizers of this invention.
実施例1
前記した細菌バイオマス肥料を、マツシュルーム生産に
おいて、コンポストおよびコンポスト化工程の改善に対
する補足栄養物として用いた。予備コンポスト化の間に
、コンポストの新鮮重量に基づき算出した0、5〜2.
0重量%の細菌バイオマス肥料を出発物質(馬こやし)
に加えた。また、0.5〜2.0%の細菌バイオマス肥
料゛をコンポスト化段階に、直接添加した。良好な品質
のコンポストが得られると同時に、収率が15〜20%
改、善され(3回の収穫について20〜24kg/zつ
、収量は、20〜30%改善された。Example 1 The bacterial biomass fertilizer described above was used as a supplementary nutrient for composting and improving the composting process in pine mushroom production. During pre-composting, 0,5-2.
Starting material: 0% by weight bacterial biomass fertilizer (Umakoyashi)
added to. Additionally, 0.5-2.0% bacterial biomass fertilizer was added directly to the composting stage. Good quality compost can be obtained with a yield of 15-20%.
(20-24 kg/z for 3 harvests, yield improved by 20-30%).
実施例2
わら基質(例えは、干し草)からなるいわゆる合成コン
ポストのコンポスト化または予備コンポスト化の間に、
細菌バイオマス肥料を用いることにより、コンポスト化
工程の改善(迅速な分解時間)、高い収率(15〜25
%)、マツノコルームの品質改善および迅速な収穫の開
始が達成された。用いた細菌バイオマスの必要な量(J
、出発基質に依存するが、湿潤コンポストに基づき、2
〜5%である。Example 2 During the composting or pre-composting of a so-called synthetic compost consisting of a straw substrate (eg hay),
By using bacterial biomass fertilizer, improved composting process (fast decomposition time), high yield (15-25
%), an improvement in the quality of the pine nuts and a faster start of harvest were achieved. The required amount of bacterial biomass used (J
, depending on the starting substrate, but based on wet compost, 2
~5%.
害美性夫
ケーノングまたはスパウニンク(種菌接種)の間に細菌
バイオマスを補足することにより、高い収率が得られた
。マルヂンク′の間に、少量の細菌バイオマス(例えば
、100〜200 !7/x2)を加えた場合でも、マ
ツノコルームは、被覆土壌を介し急速に増殖し、従って
早期の収穫と25〜30%もの高い収率(収穫1〜4)
が得られた。また、品質も改善された。結果を以下の第
1表に示す。High yields were obtained by supplementing bacterial biomass during inoculation or spawning. Even if a small amount of bacterial biomass (e.g. 100-200 !7/x2) is added during the marjink', the pine columbium multiplies rapidly through the cover soil, thus leading to an early harvest and a high yield of as much as 25-30%. Yield (harvest 1-4)
was gotten. Quality has also been improved. The results are shown in Table 1 below.
第1表
収率: I m2当たりの新鮮なマノノコルームの重量
Ckq)C添加した細菌バイオマス量 1辺′当たり1
65y)
テストの 56 60 68 73 76
B1 84’BBM−細菌ハイオマス肥料
叉鳳桝ニ
オイスター(oyster)マツノコルーム〔プレウU
タス・オノ、トレ7ツス(Pleurotus−ost
reatus) 〕 を、 地下室のわら床」二て培養
し、実験した。わら床は、約30に9を計り取り、プラ
スデックザック中にて水で48時間濡らし、その後地下
室で乾燥し、次いでマツツユルーム菌糸を吹き付けて調
製した。1ベールのわら床を細菌バイオマス409で肥
料化し、付加的な栄養物を有しない対照を育成した。ま
ず、水散布を、1週間の間隔にて水道水によりわら床1
ヘール当たり約2.5i2の割合で、行った。約4kg
/m’
週間後、間隔を2週間に延長した。結果を以下の第2表
に示す。Table 1 Yield: I Weight of fresh manokorum per m2 Ckq) Amount of C added bacterial biomass 1 per side'
65y) Test 56 60 68 73 76
B1 84'BBM-Bacterial Hiomas Fertilizer Oyster Pine Tree Room
Pleurotus-ost
reatus)] was cultured on a straw bed in a basement, and experiments were conducted. Straw beds were prepared by measuring approximately 9 in 30 and soaking in water for 48 hours in a plus deck sack, then drying in the basement, and then spraying with Pine Tree Room mycelium. One bale of straw bed was fertilized with bacterial biomass 409 and a control without additional nutrients was grown. First, sprinkle water on the straw bed with tap water at intervals of one week.
A rate of about 2.5 i2 per hel was used. Approximately 4kg
/m' weeks later, the interval was extended to 2 weeks. The results are shown in Table 2 below.
」劣Δ
新鮮なマンツユルーム収穫物の重量(9)88年7り′
88年8月゛88年9月′88年9月゛88年10月
全量ロ
ームコンポストを、対照として用いた。以下に、収率増
加を示す。``Inferior Δ Weight of fresh mantuyulum harvest (9) 1988 7ri'
August 1988 September 1988 September 1988 October 1988
Whole volume loam compost was used as a control. The yield increase is shown below.
寒±Δ
収率・kg/m’(新鮮なマツノコルーム重量)収穫物
対照 BBM* *
l 4% 28% 4
*
2%
BBM 905 1.480 1.3
85 0 1.[145536%の収率改
善とは別に、さらに、収穫物形成の早期開始(約3週間
)が得られた。観察期間の間に、収穫物の総数は、細菌
バイオマスにより2倍となった。前記マツノコルーム培
養と同様に、非肥料化・対照はやがて部分的に収穫物の
損失が生じて相殺されたが、培養の短縮という大きな利
点は維持されるようである。Cold ±Δ Yield/kg/m' (Fresh pine seed room weight) Harvest Control BBM * * l 4% 28% 4 * 2% BBM 905 1.480 1.3
85 0 1. [Apart from a yield improvement of 145536%, an earlier onset of crop formation (approximately 3 weeks) was also obtained. During the observation period, the total number of crops was doubled due to bacterial biomass. Similar to the pine seed room culture, the unfertilized control was eventually offset by partial yield losses, but the significant advantage of shortened culture appears to be maintained.
失旌桝且
種々のタイプのマツノコルーム〔アガリクス(Agar
icus) :]の生産における真菌類の菌糸体の接種
の間に直接栄養源として用いるへく、細菌バイオマス肥
料を種々の濃度で混合した。わずかな窒素含量と約68
%の水分を有する従来からのマノソユル448】
収率kg/m’ (マノノコルームの新鮮な重量)湿
潤コンポスト?こ対する%
実施例6
種々のタイプのマツノコルーム〔アガリクス(Agar
icus) )の生産にお(Jる真菌類の菌糸体接種の
間に直接栄養源として用いるべく、細菌バイオマス肥料
を乾燥コンポストに対し1.4%の濃度で混合した。生
産に際し、約30トンのコンポストについて16個の配
合をテストした。以下の第4表に示すように、平均して
、1m2当たりマツノコルーム2 、5 kgの収率増
加が得られた。Various types of pine tree room [Agaricus (Agar)]
Bacterial biomass fertilizer was mixed at various concentrations to be used as a direct nutrient source during the inoculation of fungal mycelium in the production of A. icus). With a slight nitrogen content about 68
448] yield kg/m' (fresh weight of manosoylum) wet compost? Example 6 Various types of pine nuts [Agar
Bacterial biomass fertilizer was mixed with dry compost at a concentration of 1.4% for use as a direct nutrient source during mycelium inoculation of fungi (J. icus). During production, approximately 30 tons of 16 formulations were tested for composting.On average, a yield increase of 2.5 kg of pine wood per m2 was obtained, as shown in Table 4 below.
見上Δ
収率・kg/m’、(新鮮なマツシュルーム重量)収穫
物 1.4%細菌バイオマス含有9 対照2
8.00” 7.51”3 2
.67” 2.2’8”全量: 2
+、32” 18.82”%
l 13.30 100.00* 乾
燥コンポストに対する%
**8個の試料の平均値
実施例7
0.2%、0.5%および0.8%のホルムアルデヒド
を含有する、11当たり1.4kgの細菌バイオマス肥
料(−湿潤コンポストに対し1.4%の細菌バイオマス
)、および02%、05%および08%のホルムアルデ
ヒド含有する、■が当たり2 、8 kgの細菌バイオ
マス肥料(−湿潤コンポストに対し2.8%の細菌バイ
オマス)を添加することにより、以下の第5表に示す結
果を得た。Appearance Δ Yield kg/m', (fresh pine mushroom weight) Harvest 1.4% bacterial biomass content 9 Control 2
8.00” 7.51”3 2
.. 67"2.2'8" total amount: 2
+, 32” 18.82”%
l 13.30 100.00*% of dry compost **Average of 8 samples Example 7 1.4 kg per 11 containing 0.2%, 0.5% and 0.8% formaldehyde Bacterial biomass fertilizer (-1.4% bacterial biomass for wet compost) and 2,8 kg of bacterial biomass fertilizer (-2 for wet compost) containing 02%, 05% and 08% formaldehyde. By adding .8% bacterial biomass), the results shown in Table 5 below were obtained.
第3の混合ののち、コンポスト塊は、未だなお水分含量
約72%の約160トンであった。コンポスト塊を、低
温殺菌により水分含量71%の約140トンに減少させ
た。最後に、菌糸接種時では、約68%の水分含量のコ
ンポスト120トンであった。菌糸接種には1%菌糸体
を用いた。After the third mixing, the compost mass was approximately 160 tons, still with a moisture content of approximately 72%. The compost mass was reduced to approximately 140 tons with a moisture content of 71% by pasteurization. Finally, at the time of mycelial inoculation, there was 120 tons of compost with a moisture content of approximately 68%. 1% mycelium was used for mycelial inoculation.
第6表において、ケーシング工程およびその後の結実に
おける被覆土壌の開口および表土による被覆のような、
付加的な工程を示すことができる。In Table 6, such as the opening of the cover soil and the cover by topsoil during the casing process and subsequent fruiting,
Additional steps may be indicated.
3回の収穫の間、細菌バイオマス肥料の付加的な使用の
成功は、該細菌バイオマス肥料補足物を未使用の場合の
年平均生産高と比較すれば、明白である。The success of the additional use of bacterial biomass fertilizer during three harvests is evident when comparing the annual average yield without the use of the bacterial biomass fertilizer supplement.
また、品質も改善され、一級品は65%から85%に増
加した。Quality has also improved, with first-class products increasing from 65% to 85%.
実施例9
別の装置において、実施例8と同様に、同量のコンポス
トおよび添加物を用いたが、第3混合において、細菌バ
イオマスのみを、湿潤コンポストの0.35%、0.7
%および12%量で用いた。Example 9 In a separate device, the same amounts of compost and additives were used as in Example 8, but in the third mix, only bacterial biomass was mixed with 0.35% of wet compost, 0.7
% and 12% amounts were used.
基晃表
収率kg/m’(新鮮なマツシュルーム重量)ホルムア
ルデヒド 対照
02% 05% 08%
BBMl、4% 33.1 31.6 28,6 3
0.1BBM2.8% 36,8 38,5 33.4
34 4対照 −−−22,0
実施例8
約62%の水分を含む安定な肥料の連続的供給物100
トンに対し、水40m3を添加し、次いで細菌バイオマ
ス肥料1200g(湿潤コンポストの約1%)を混合し
て予備コンポスト化を行った。Motoaki table yield kg/m' (fresh pine mushroom weight) Formaldehyde Control 02% 05% 08% BBMl, 4% 33.1 31.6 28,6 3
0.1BBM2.8% 36.8 38.5 33.4
34 4 Control ---22,0 Example 8 Continuous feed of stable fertilizer containing about 62% moisture 100
For each ton, 40 m3 of water was added and then 1200 g of bacterial biomass fertilizer (approximately 1% of the wet compost) was mixed for pre-composting.
この予備コンポストは、2回混合した6ので、水分含量
69%の151トンに相当する。これらのコンポスト化
用の添加ののち、再び水+7i’を加え、カカオ豆の殻
1450に9および大豆ミール580に9を混合した。This precompost was mixed twice and thus corresponds to 151 tons with a moisture content of 69%. After these composting additions, water + 7i' was again added and 9 in cocoa bean shells 1450 and 9 in soybean meal 580 were mixed.
第1の混合では、硫酸アンモニウム980kgを(−1
加的に混合し、水分含量72%のコンポストl 701
−ンを得た。第2の混合では、石灰2950kyを混合
してpHを調整し、水分含量約73%のコンポスト約1
60トンを得た。In the first mix, 980 kg of ammonium sulfate (-1
Additively mixed compost with a moisture content of 72% l 701
-I got the answer. In the second mix, 2950 ky of lime was mixed to adjust the pH and the compost with a moisture content of about 73% was mixed with about 1 ky of lime.
Obtained 60 tons.
また、収穫量および品質の改善が得られた。統計的条件
を立案できないので、年平均生産高との比較だけが可能
である。Also, improvements in yield and quality were obtained. Since statistical conditions cannot be formulated, only comparisons can be made with annual average production.
第6表
実施例8および実施例9の生産計画
5 混合
低温殺菌
接種
開口
表土の被覆
結実
収穫段階
第1フラツシング
第2フラツシング
第37ラツンング
菌糸体
特許出願人 ビオヘミ−・ゲゼルシャフト・ミツト・ベ
シュレンクテル・ハフラングTable 6 Production Plan 5 for Examples 8 and 9 Mixed Pasteurization Inoculation Open Topsoil Covering Fruiting Harvest Stage 1st Flushing 2nd Flushing 37th Ratsung Mycelium Patent Applicant Biohemie Gesellschaft Mitsut Beschlenkter Haflang
Claims (1)
することを特徴とする製法。 2、細菌バイオマスが、抗生物質の発酵において得られ
る液相を付加的に発酵させることによって調製される、
請求項1記載の製法。 3、肥料が、該栄養物の放出を遅延させるに有効な量の
ホルムアルデヒドを含有する、請求項1または2記載の
製法。 4、肥料が、90〜97乾燥重量%からなり、少なくと
も55重量%の有機物質、4.9〜6.1重量%の有機
結合窒素、3.9〜5重量%のP_2O_5、2.9〜
3.7重量%のK_2O、7〜9重量%のCaOおよび
0.8〜1.4重量%のMgOを含有する、請求項1〜
3の1つに記載の製法。 5、肥料が、細菌バイオマス約94重量%と苦土カリ肥
料約6重量%の混合物からなる、請求項1〜4の1つに
記載の製法。 6、抗生物質がペニシリンである、請求項2〜5の1つ
に記載の製法。 7、肥料を、予備コンポスト化、コンポスト化および/
または種菌接種において用いる、請求項1〜6の1つに
記載の製法。 8、細菌バイオマスと苦土カリ肥料からなり実質的に重
金属を含まない肥料であって、 該細菌バイオマスが、抗生物質の発酵において得られる
液相を付加的に発酵させることによって調製される肥料
。 9、90〜97乾燥重量%からなり、少なくとも55重
量%の有機物質、4.9〜6.1重量%の有機結合窒素
、3.9〜5重量%のP_2O_5、2.9〜3.7重
量%のK_2O、7〜9重量%のCaOおよび0.8〜
1.4重量%のMgOを含有する混合物からなる、請求
項8記載の肥料。 10、細菌バイオマス約94重量%と苦土カリ肥料約6
重量%の混合物からなる、請求項8または9記載の肥料
。 11、抗生物質がペニシリンである、請求項8〜10の
1つに記載の肥料。 12、細菌バイオマスを製造するにあたり、抗生物質の
発酵において得られる液相を中和剤で処理し、次いで得
られた液相を付加的な発酵に付して該細菌バイオマスを
得ることを特徴とする製法。 13、さらに、付加的な該発酵前に、上記液相と種々の
発酵工程からの有機廃棄物を合する、請求項12記載の
製法。 14、付加的な該発酵が、酸素の存在下にて約30℃で
行う、請求項12または13記載の製法。 15、抗生物質がペニシリンである、請求項12〜14
記載の製法。[Claims] 1. A production method characterized in that, in producing mushrooms, a fertilizer made of bacterial biomass is used as a supplementary nutrient. 2. Bacterial biomass is prepared by additionally fermenting the liquid phase obtained in the fermentation of antibiotics.
The manufacturing method according to claim 1. 3. The method of claim 1 or 2, wherein the fertilizer contains formaldehyde in an amount effective to retard the release of the nutrients. 4. The fertilizer consists of 90-97% by dry weight, at least 55% by weight organic matter, 4.9-6.1% by weight organically bound nitrogen, 3.9-5% by weight P_2O_5, 2.9-5% by weight
Claims 1 to 3 containing 3.7% by weight K_2O, 7-9% by weight CaO and 0.8-1.4% by weight MgO.
The manufacturing method described in one of 3. 5. The method according to one of claims 1 to 4, wherein the fertilizer consists of a mixture of about 94% by weight of bacterial biomass and about 6% by weight of magnesia potassium fertilizer. 6. The production method according to one of claims 2 to 5, wherein the antibiotic is penicillin. 7. Pre-composting, composting and/or composting of fertilizers
Or the production method according to one of claims 1 to 6, which is used in seed inoculation. 8. A fertilizer consisting of bacterial biomass and magnesium potassium fertilizer and substantially free of heavy metals, wherein the bacterial biomass is prepared by additionally fermenting a liquid phase obtained in the fermentation of antibiotics. 9, consisting of 90-97% by dry weight, at least 55% by weight organic matter, 4.9-6.1% by weight organically bound nitrogen, 3.9-5% by weight P_2O_5, 2.9-3.7 wt% K_2O, 7-9 wt% CaO and 0.8-
Fertilizer according to claim 8, consisting of a mixture containing 1.4% by weight of MgO. 10. Bacterial biomass approximately 94% by weight and magnesium potassium fertilizer approximately 6%
Fertilizer according to claim 8 or 9, consisting of a mixture of % by weight. 11. Fertilizer according to one of claims 8 to 10, wherein the antibiotic is penicillin. 12. In producing bacterial biomass, the liquid phase obtained in the fermentation of antibiotics is treated with a neutralizing agent, and the obtained liquid phase is then subjected to additional fermentation to obtain the bacterial biomass. The manufacturing method. 13. The method of claim 12, further comprising combining said liquid phase with organic wastes from various fermentation steps prior to said additional fermentation. 14. The method of claim 12 or 13, wherein the additional fermentation is carried out at about 30°C in the presence of oxygen. 15. Claims 12 to 14, wherein the antibiotic is penicillin.
Manufacturing method described.
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
AT265488 | 1988-10-27 | ||
AT2654/88 | 1988-10-27 |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH02177821A true JPH02177821A (en) | 1990-07-10 |
Family
ID=3538158
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP1279614A Pending JPH02177821A (en) | 1988-10-27 | 1989-10-26 | Bacterial biomass fertilizer |
Country Status (7)
Country | Link |
---|---|
EP (1) | EP0369223A1 (en) |
JP (1) | JPH02177821A (en) |
CA (1) | CA2001501A1 (en) |
DK (1) | DK531489A (en) |
FI (1) | FI895082A0 (en) |
NO (1) | NO894243L (en) |
PT (1) | PT92100A (en) |
Families Citing this family (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
IE62649B1 (en) * | 1990-07-06 | 1995-02-22 | Clancy Martin | A natural and renewable organic compost/fertilizer |
CN103204723A (en) * | 2013-04-07 | 2013-07-17 | 邬金飞 | Mushroom cultivated species compost and preparation method thereof |
CN112811957A (en) * | 2021-01-26 | 2021-05-18 | 中国医学科学院药用植物研究所云南分所 | Biological bacterial fertilizer and preparation method and application thereof |
Family Cites Families (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
GB854918A (en) * | 1956-02-06 | 1960-11-23 | Jaroslav Vintika | Azotobacter concentrates obtained by submerged aerobic fermentation |
US3942969A (en) * | 1974-05-21 | 1976-03-09 | Carroll Jr Alban David | Delayed release nutrients for mushroom culture |
US4333757A (en) * | 1980-03-21 | 1982-06-08 | The United States Of America As Represented By The Secretary Of Agriculture | Mushroom-growing medium |
DD154930A3 (en) * | 1980-10-21 | 1982-05-05 | Wolfgang Sonnenkalb | GROWTH STIMULATOR FOR CHAMIGNON GROWTH |
DE3345635A1 (en) * | 1983-12-16 | 1985-06-27 | Volz, Otto, 8870 Günzburg | Decomposing agent for composting, as well as method and device |
-
1989
- 1989-10-25 PT PT92100A patent/PT92100A/en not_active Application Discontinuation
- 1989-10-25 CA CA002001501A patent/CA2001501A1/en not_active Abandoned
- 1989-10-25 DK DK531489A patent/DK531489A/en not_active Application Discontinuation
- 1989-10-25 NO NO89894243A patent/NO894243L/en unknown
- 1989-10-26 EP EP89119914A patent/EP0369223A1/en not_active Withdrawn
- 1989-10-26 FI FI895082A patent/FI895082A0/en not_active Application Discontinuation
- 1989-10-26 JP JP1279614A patent/JPH02177821A/en active Pending
Also Published As
Publication number | Publication date |
---|---|
DK531489A (en) | 1990-04-28 |
DK531489D0 (en) | 1989-10-25 |
EP0369223A1 (en) | 1990-05-23 |
NO894243D0 (en) | 1989-10-25 |
NO894243L (en) | 1990-04-30 |
CA2001501A1 (en) | 1990-04-27 |
PT92100A (en) | 1990-04-30 |
FI895082A0 (en) | 1989-10-26 |
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